BMP testingBy-products of the agri-food industry

Oil refining residues (gums, condensates, spent earth) — BMP: 5 studies, weighted mean 714 m³ CH₄/t VS

Oil refining residues (gums, condensates, bleaching earth) are concentrates of fats and lipids with a high gas potential and LCFA risk.

CH₄ ≈ 63 % (estimate)

Published Updated 3 min readFeedstockData Editorial Team

Photo Khalid Mahmood / Wikimedia Commons, licence CC BY-SA 3.0, source file; changes: cropping

Weighted mean
714m³ CH₄/t VS
Range
426–866m³ CH₄/t VS
Records
5studies
Publications
2sources
Temperatures
35 °C, 38 °Cof the test

Methane in biogas

High methane content · ≈ 6.3 kWh/m³ of biogas

estimate from the substrate type The collected studies contain no measurement. The interval follows from the approximate composition (carbohydrate-dominated (no protein or fat characteristics); fat-rich (process classification)) and the yields of compound groups according to FNR.

How we calculate it and what the zones mean

Rating for biogas plants

not rated — editorial rating for biogas plants

Not rated: no dry matter or volatile solids in the data. We calculate the rating when the dry matter and volatile solids of the material are known.

Editorial rating per the methodology

Add to the co-digestion calculator CSV data

BMP curves from 5 studies

Weighted mean Individual records

BMP curves: Oil refining residues (gums, condensates, spent earth)Cumulative methane production over time for 5 records and the weighted mean of 714 m³ CH₄/t VS. 5 of the curves are model curves (first-order kinetics).020040060080010000510152025303540time [d]m³ CH₄/t VSDubrovskis i Plume (2024): 814 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 1: 426 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 2: 504 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 3: 664 m³ CH₄/t VS (model curve)Kouas et al. (2017) · 4: 866 m³ CH₄/t VS (model curve)mean714

Dashed lines are a model curve (first-order kinetics, B(t) = B₀·(1 − e−kt)); the end point comes from the publication. All curves are model curves.

Cumulative methane production over the test [m³ CH₄/t VS]. The thick line is the weighted mean of all records (714); dots mark the end values given in the publications. Point at the chart to read values; click a legend item to hide or show a record.

Records and sources

Download CSV
SourceBMP
m³ CH₄/t VS
TemperatureSampleCurve
Dubrovskis i Plume (2024) DOI81438 °C · mesophilicRapeseed oil refining by-productend point (model curve)
Kouas et al. (2017) · 1 DOI42635 °C · mesophiliccondensate (sunflower oil)end point (model curve)
Kouas et al. (2017) · 2 DOI50435 °C · mesophiliccondensate (palm oil)end point (model curve)
Kouas et al. (2017) · 3 DOI66435 °C · mesophilicoilend point (model curve)
Kouas et al. (2017) · 4 DOI86635 °C · mesophilicgumend point (model curve)
Weighted mean714arithmetic mean 655, SD 190

Process properties

  • fat-rich
  • tendency to foam
  • forms a floating layer
  • low in nitrogen
  • variable composition
  • editorial classification

Low confidence: the description is based on general characteristics of the substrate group, not on studies of this material. Treat it as a hint to be verified.

Advantages

  • Methane potential in the Substraty.pl BMP dataset: weighted mean 714.5 m³ CH₄/t VS (SD 190.5; 5 records, 2 sources).
  • A lipid concentrate of high potential (Long et al. 2012).

Drawbacks and risks

  • Free LCFA inhibit methanogenesis and cause flotation (Long et al. 2012; Elsamadony et al. 2021).
  • Low N content requires a slurry base.

Co-digestion — what to combine it with, what to watch out for

Dosing

No source-based threshold; apply the shared lipid limit, start low.

Introduce gradually, starting with a small dose and monitoring the process (e.g. FOS/TAC, pH, gas composition).

The co-digestion calculator will assess a specific mixture containing this substrate.

What it is and where it comes from

The refining of vegetable oils consists in removing impurities and undesirable components from crude oil. The successive stages generate wastes: gums (degumming, rich in phospholipids), deodorisation condensates (free fatty acids and volatile compounds), and spent bleaching and filtration earth, on which oil is deposited. In Poland rapeseed and sunflower oil refineries are significant, and the materials described here include sunflower and palm oil condensates and earth from the winterisation of sunflower oil.

Properties relevant to digestion

The main components are lipids in various forms: phospholipids in gums, free fatty acids in condensates, and oil adsorbed in earth. Such wastes have a very high energy potential, because fats give more methane per unit of dry matter than carbohydrates. At the same time free long-chain fatty acids are inhibitors of methanogenesis and cause foaming and flotation of biomass. Bleaching earth additionally contains mineral components which do not ferment. The low nitrogen content requires combining with slurry or protein-rich material.

How to read the spread of results

The dataset contains several records from a small number of sources, mainly one study, so independent verification is limited. They describe different materials: condensates, earth and gums, which have different compositions, so the variability stems more from the type of waste than from measurement error. The result is also affected by the type of oil (sunflower, palm, rapeseed), the degree of refining, the share of adsorbed fat in the earth, size reduction, the inoculum and the adaptation of the microflora to lipids.

In biogas plant practice

Refining wastes are used at a limited share, dosed gradually and evenly to avoid lipid shock. Combining with slurry and constant monitoring of volatile acids and gas production are recommended. Fatty materials may require heating for pumping. Waste from the food industry is waste, so its acceptance requires appropriate authorisations. Spent earth has limited use because of its mineral content.

It should be noted that the internal diversity of this group is so great that an average for it has limited practical value; in planning the dose, the analysis of the specific batch should be relied on, especially its fatty acid and water content.

Methodology in brief

BMP is the amount of methane obtained from volatile solids (VS) in a batch test, given in m³ CH₄ per tonne of VS (numerically the same as NmL CH₄/g VS in the publications) and converted to normal conditions (0 °C, 101.325 kPa). The weighted mean gives each publication a total weight of 1, split equally between its results for the substrate — a paper testing twenty varieties does not outweigh a paper with a single sample. In inter-laboratory programmes the unit is the laboratory (total weight 1), and within it the weight of a test grows with the number of bottles (replicates). Results after pretreatment (e.g. thermal, chemical, enzymatic) are shown separately and are not included in the mean.

Solid lines are curves measured in the tests. Where a publication gives only the final result, we draw a first-order kinetic model, B(t) = B₀·(1 − e−kt): only the end point comes from the publication, and the shape of the curve serves purely as visualisation — do not read the production on a particular day from it. For this substrate k = 0.091 d−1 was assumed (no kinetic data for the group – the median of all available rate constants k (93 values) was used).

The statistics describe the spread of published results — a descriptive compilation, not a meta-analysis or a guarantee of plant yield.

Full methodology and correction policy

Bibliography

  1. Dubrovskis, V.; Plume, I. (2024). Biogas potential from biodiesel production residues. Engineering for Rural Development 23. DOI: 10.22616/erdev.2024.23.tf104 DOI
  2. Kouas, M.; Torrijos, M.; Sousbie, P.; Steyer, J.P.; Sayadi, S.; Harmand, J. (2017). Robust assessment of both biochemical methane potential and degradation kinetics of solid residues in successive batches. Waste Management 70, 59–70. DOI: 10.1016/j.wasman.2017.09.001 DOI

All sources of the site: bibliography.